EP1527809A1 - Dispositif pour la purification photocatalytique de l'air - Google Patents

Dispositif pour la purification photocatalytique de l'air Download PDF

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Publication number
EP1527809A1
EP1527809A1 EP04025764A EP04025764A EP1527809A1 EP 1527809 A1 EP1527809 A1 EP 1527809A1 EP 04025764 A EP04025764 A EP 04025764A EP 04025764 A EP04025764 A EP 04025764A EP 1527809 A1 EP1527809 A1 EP 1527809A1
Authority
EP
European Patent Office
Prior art keywords
photocatalytic reaction
reaction device
casing
vanes
intake port
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
EP04025764A
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German (de)
English (en)
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EP1527809B1 (fr
Inventor
Takafumi Nakahama
Kazuo Sato
Kuniyuki Araki
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Toshiba Corp
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Toshiba Corp
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Publication of EP1527809A1 publication Critical patent/EP1527809A1/fr
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    • A—HUMAN NECESSITIES
    • A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
    • A61L9/00—Disinfection, sterilisation or deodorisation of air
    • A61L9/16—Disinfection, sterilisation or deodorisation of air using physical phenomena
    • A61L9/18—Radiation
    • A61L9/20—Ultraviolet radiation
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86—Catalytic processes
    • B01D53/8671—Removing components of defined structure not provided for in B01D53/8603 - B01D53/8668
    • B01D53/8675—Ozone
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34—Chemical or biological purification of waste gases
    • B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • B01D53/86—Catalytic processes
    • B01D53/8678—Removing components of undefined structure
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F24—HEATING; RANGES; VENTILATING
    • F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
    • F24F7/00—Ventilation
    • F24F7/04—Ventilation with ducting systems, e.g. by double walls; with natural circulation
    • F24F7/06—Ventilation with ducting systems, e.g. by double walls; with natural circulation with forced air circulation, e.g. by fan positioning of a ventilator in or against a conduit
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F24—HEATING; RANGES; VENTILATING
    • F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
    • F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
    • F24F8/10—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by separation, e.g. by filtering
    • F24F8/15—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by separation, e.g. by filtering by chemical means
    • F24F8/167—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by separation, e.g. by filtering by chemical means using catalytic reactions
    • F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F24—HEATING; RANGES; VENTILATING
    • F24F—AIR-CONDITIONING; AIR-HUMIDIFICATION; VENTILATION; USE OF AIR CURRENTS FOR SCREENING
    • F24F8/00—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying
    • F24F8/20—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation
    • F24F8/22—Treatment, e.g. purification, of air supplied to human living or working spaces otherwise than by heating, cooling, humidifying or drying by sterilisation using UV light
    • A—HUMAN NECESSITIES
    • A61—MEDICAL OR VETERINARY SCIENCE; HYGIENE
    • A61L—METHODS OR APPARATUS FOR STERILISING MATERIALS OR OBJECTS IN GENERAL; DISINFECTION, STERILISATION OR DEODORISATION OF AIR; CHEMICAL ASPECTS OF BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES; MATERIALS FOR BANDAGES, DRESSINGS, ABSORBENT PADS OR SURGICAL ARTICLES
    • A61L2209/00—Aspects relating to disinfection, sterilisation or deodorisation of air
    • A61L2209/10—Apparatus features
    • A61L2209/14—Filtering means
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2255/00—Catalysts
    • B01D2255/80—Type of catalytic reaction
    • B01D2255/802—Photocatalytic
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01D—SEPARATION
    • B01D2259/00—Type of treatment
    • B01D2259/80—Employing electric, magnetic, electromagnetic or wave energy, or particle radiation
    • B01D2259/804—UV light

Definitions

  • the present invention relates to a photocatalytic reaction device comprising a photocatalyst, a photocatalyst carrier that carries (or supports) this photocatalyst and a blower (an air blower), whereby substances that come into contact with, adhere to or approach the photocatalyst are decomposed by a photocatalytic reaction.
  • Devices for cleaning air (or purifying air), comprising a dust collecting filter or deodorizing filter and a blower, are well known.
  • An example is the device disclosed in Laid-open Japanese Patent Application No. Tokkai 2003-106581.
  • a photocatalyst and a photocatalyst carrier that carries this photocatalyst are also known, an example being Laid-open Japanese Patent Application No. Tokkai H. 11-335187.
  • Photocatalytic reaction devices are also already known comprising a photocatalyst, a photocatalyst carrier made of a porous substance that carries this photocatalyst, and a blower, wherein substances coming into contact with, adhering to or approaching the photocatalyst are decomposed by a photocatalytic reaction.
  • Figure 1A A prior art of such a photocatalytic reaction device is shown in Figure 1A and Figure 1B.
  • the lower Figure ( Figure 1B) shows a cross-sectional view including the axis (axis center) of a series of blower vanes
  • the upper Figure ( Figure 1A) shows a cross-section in the direction perpendicular to the aforementioned axis, including the blower drive motor.
  • the cross-section of the hub of the blower is not shown in the upper Figure ( Figure 1A).
  • fluid that flows in from an intake port (inlet port, suction port) 2 provided in the casing 1 flows out from a discharge port 3 arranged in the face where the intake port 2 is provided, or in a location in a face other than this.
  • a centrifugal type blower 4 is provided, having a series of vanes 5, in the vicinity of the intake port 2 inside the casing 1 and a photocatalyst carrier 6 that carries a photocatalyst is provided at the discharge port.
  • a blower drive motor 7 and a motor power source 8 are provided within the casing 1.
  • substances in the air coming into contact with, adhering to or approaching the catalyst carried on the photocatalyst carrier 6, such as for example impurities, are decomposed by a reaction such as oxidation or reduction.
  • high voltage from a high-voltage power source 12 shown in these Figures is applied to high-voltage terminals 11a, 11b arranged on the upstream side and downstream side of the photocatalyst carrier 6 and electrical discharge is produced between these two terminals.
  • Ultraviolet light is thereby generated, that promotes the decomposition action of the photocatalyst.
  • Impurities in the air undergo oxidative decomposition by the ozone that is then generated by the ultraviolet light.
  • Ozone that is not used in this decomposition is absorbed by an ozone decomposition filter 13 arranged on the inside of the discharge port 3.
  • the series of vanes 5 generates fluid noise, but, as shown in Figure 1A and Figure 1B, the photocatalyst carrier 6 and ozone decomposition filter 13 are arranged on the side of the discharge port 3, so noise is attenuated and the noise propagated to the outside from the discharge port 3 can thereby be reduced.
  • the noise from the intake port 2 was propagated to the outside with scarcely any attenuation.
  • one object of the present invention is to provide a novel photocatalytic reaction device having a high decomposition treatment capability so as to be capable of treating impurities present in the air in large quantity.
  • a further object of the present invention is to provide a photocatalytic reaction device of low noise.
  • a photocatalytic reaction device is constructed as follows. Specifically, a photocatalytic reaction device according to the present invention comprises an intake port formed in a casing, discharge ports formed in a side face of the casing different from this intake port, a centrifugal type blower for feeding fluid flowing in from the intake port to the discharge ports, and a photocatalyst carrier that carries photocatalyst and is provided in the fluid path between the intake port and the discharge ports, wherein the discharge ports are formed over the entire surface of the side face of the casing or are formed in a plurality of locations of the side face of the casing.
  • a photocatalytic reaction device having a high decomposition treatment capability, that is capable of treating impurities present in large quantity in air.
  • noise can be reduced by adopting a construction wherein the photocatalyst carrier is provided around the intake port and the series of vanes of the centrifugal type blower is provided at the outer periphery of the photocatalyst carrier, or the photocatalyst carrier is provided facing the intake port and the series of vanes of the centrifugal type blower is arranged facing the opposite side of this photocatalyst carrier to that of the intake port and ozone decomposition filters are provided at the outer periphery of the series of vanes of the centrifugal type blower.
  • Figures B show a cross-section containing the axis of the series of vanes of the blower while the upper Figures ( Figures A) show a cross-section in the direction perpendicular to the aforesaid axis, containing the blower drive motor.
  • the cross-section of the hub of the blower is not shown in the upper Figures ( Figures A).
  • Figure 2A and Figure 2B are views showing the construction of a photocatalytic reaction device according to a first embodiment of the present invention.
  • an intake port 2 having apertures in the form of a mesh is formed in the middle of the upper surface of a cylindrical casing 1. Also, a plurality of discharge ports 3 having apertures in the form of a mesh are formed in a side face of the casing 1 different from that in which this intake port 2 is formed.
  • a series of vanes 5 of a centrifugal type blower 4 for delivering air flowing in from the intake port 2 to the discharge ports 3 is arranged around the intake port 2 within the casing 1 and an annular photocatalyst carrier 6 made of a porous body that carries a photocatalyst is arranged at the outer periphery of the series of vanes 5 of this centrifugal type blower 4.
  • a construction is adopted in which the discharge ports 3 are arranged on the side face of the casing 1 of the photocatalytic reaction device 9, at least two discharge ports being arranged in directions differing by practically 180° in the radial direction of the series of vanes 5 of the centrifugal type blower 4, or a plurality of discharge ports being arranged around the centrifugal type blower 4, or the discharge ports being arranged continuously over the entire periphery of the side face of the casing 1.
  • the partition 20 that was conventionally provided in the vicinity of the series of vanes 5 is absent, so that, as shown in Figure 32, the fan characteristic is shifted from C0 to a characteristic C1 providing a large flow rate and a large static pressure. Also, due to increase of the area of the flow paths to the discharge ports 3, the airflow resistance is decreased from R0 to R1. As a result, the operating flow rate increases to Q1 from the conventional value of Q0 so that a higher decomposition treatment capability than conventionally is displayed in respect of impurities in the air.
  • Figure 3A and Figure 3B are views showing the construction of a photocatalytic reaction device according to a second embodiment of the present invention.
  • a photocatalytic reaction device has a construction wherein, in the first embodiment described above, high-voltage terminals 11a, 11b connected with a high-voltage power source 12 are arranged at the outer periphery and inner periphery of the photocatalyst carrier 6 and ozone decomposition filters 13 are arranged on the side of these nearest the discharge ports 3.
  • the decomposition effect of the photocatalyst is increased by the generation of ultraviolet light by discharge between the high-voltage terminals 11a, 11b.
  • the high-voltage terminals 11a, 11b constitute ultraviolet ray generating means (generating unit).
  • the ozone that is generated by this ultraviolet light then performs oxidative decomposition of impurities in the air.
  • Ozone that is not used for this decomposition is absorbed by ozone decomposition filters 13.
  • ozone decomposition filters 13 Since there is no outflow of excess ozone from the discharge ports 3, sufficient ozone to decompose the impurities in the air can be generated, so that the device according to this embodiment shows a decomposition treatment capability higher than that of the photocatalytic reaction device of the first embodiment, described above.
  • Figure 4A and Figure 4B are views showing the construction of a photocatalytic reaction device according to a third embodiment of the present invention.
  • the photocatalyst carrier 6 was arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4, but, in this third embodiment, the photocatalyst carrier 6 carrying the photocatalyst is arranged around the intake port 2 within the casing 1 and the series of vanes 5 of the centrifugal type blower 4 is arranged at the outer periphery of the photocatalytic reaction photocatalyst carrier 6.
  • the external diameter of the series of vanes 5 can be increased compared with the prior art construction, in which the series of vanes 5 of the centrifugal type blower 4 was arranged at the inner periphery of the photocatalyst carrier 6 (i.e. ⁇ D2 > ⁇ D1), resulting in a fan characteristic C2 providing a large static pressure.
  • the photocatalyst carrier 6 is arranged at the inner periphery of the series of vanes 5, the diameter of the photocatalyst carrier 6 being made smaller, while its thickness is made larger; thus the airflow resistance is increased from R1 to R2.
  • the flow rate Q2 is thereby increased from the flow rate Q1 of the first embodiment and a decomposition treatment capability for impurities in the air is thereby displayed that is higher than that of the first embodiment
  • Figure 5A and Figure 5B are views showing the construction of a photocatalytic reaction device according to a fourth embodiment of the present invention.
  • a photocatalytic reaction device has a construction wherein, in a photocatalytic reaction device according to the third embodiment described above, high-voltage terminals 11a, 11b connected with a high-voltage power source 12 are arranged at the outer periphery and inner periphery of the photocatalyst carrier 6.
  • Ultraviolet light is generated by discharge between the high-voltage terminals 11a, 11b. As a result, the photocatalytic reaction is promoted and a higher decomposition treatment capability for impurities in the air is displayed than in the case of the third embodiment.
  • Figure 6A and Figure 6B are views showing the construction of a photocatalytic reaction device according to a fifth embodiment of the present invention.
  • a photocatalytic reaction device has a construction wherein, in a photocatalytic reaction device according to the third embodiment described above, ultraviolet lamps 14 are arranged at the inner periphery of the photocatalyst carrier 6.
  • Ultraviolet light is directed onto the photocatalyst of the photocatalyst carrier 6 by arranging the ultraviolet lamps 14 at the inner periphery of the photocatalyst carrier 6. As a result, the photocatalytic reaction is promoted and a higher decomposition treatment capability for impurities in the air is displayed than in the case of the third embodiment.
  • Figure 7A and Figure 7B are views showing the construction of a photocatalytic reaction device according to a sixth embodiment of the present invention.
  • a photocatalytic reaction device has a construction wherein, in a photocatalytic reaction device according to the third embodiment described above, ultraviolet lamps 14 are arranged at the outer periphery of the photocatalyst carrier 6.
  • Ultraviolet light is directed onto the photocatalyst of the photocatalyst carrier 6 by arranging the ultraviolet lamps 14 at the outer periphery of the photocatalyst carrier 6.
  • ultraviolet light reflected at the surface of the series of vanes 5 arranged around the ultraviolet lamps 14 is directed onto the photocatalyst.
  • the photocatalytic reaction is promoted and a higher decomposition treatment capability for impurities in the air is displayed than in the case of the third embodiment.
  • Figure 8 is a view given in explanation of the construction of major parts of a photocatalytic reaction device according to a seventh embodiment of the present invention.
  • a photocatalytic reaction device has a construction wherein, in a photocatalytic reaction device according to the fifth embodiment described above, the negative pressure surfaces of the series of vanes 5 of the centrifugal type blower 4 are specula surfaces.
  • Figure 9 is a view given in explanation (an explanation view) of the construction of major parts of a photocatalytic reaction device according to an eighth embodiment of the present invention.
  • a photocatalytic reaction device has a construction wherein, in a photocatalytic reaction device according to the sixth embodiment described above, the negative pressure surfaces of the series of vanes 5 of the centrifugal type blower 4 are specular surfaces.
  • This photocatalytic reaction device according to the ninth embodiment has a construction wherein, in a photocatalytic reaction device according to the any of the fourth to eighth embodiments described above, ozone decomposition filters 13 are arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4 and at the inner periphery of the discharge ports 3.
  • FIGS. 10A and Figure 10B are views showing an example of the construction of this ninth embodiment.
  • any ozone generated by the ultraviolet rays that was not used for decomposition is absorbed by the ozone decomposition filters 13 arranged at the inner periphery of the discharge ports 3. Since there is no outflow of excess ozone from the discharge ports 3, sufficient ozone to decompose the impurities in the air can be generated, so that the device according to this embodiment shows a decomposition treatment capability higher than that of the photocatalytic reaction device of the fourth to the eighth embodiments, described above.
  • the series of vanes 5 generates fluid noise
  • noise is attenuated by the arrangement of the photocatalyst carrier 6 at the inner periphery and the ozone decomposition filters 13 at the outer periphery, so the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 11A and Figure 11B are views showing the construction of a photocatalytic reaction device according to a tenth embodiment of the present invention.
  • the lower Figure is a view showing a cross-section viewed in the direction of the arrows at the position of a diagonal of a practically square casing 1 in the upper Figure.
  • the shape of the casing of the photocatalytic reaction device of this tenth embodiment is practically square, when seen in projection from a direction perpendicular to the intake port, and the discharge ports 3 are arranged at the corners of this practically square casing.
  • Figure 12A and Figure 12B are views showing the construction of a photocatalytic reaction device according to an eleventh embodiment of the present invention.
  • the power source 8 for the motor of the centrifugal type blower 4 is arranged in a corner of the practically square casing 1.
  • Figure 13A and Figure 13B are views showing the construction of a photocatalytic reaction device according to a twelfth embodiment of the present invention.
  • ozone decomposition filters 13 are arranged in the corners of the practically square casing 1 in the photocatalytic reaction device of the tenth embodiment described above.
  • any ozone that is not used for decomposition is absorbed by the ozone decomposition filters 13 arranged within the discharge ports 3. Since there is no outflow of excess ozone from the discharge ports 3, sufficient ozone to decompose the impurities in the air can be generated, so that the device according to this embodiment shows a decomposition treatment capability higher than that of the photocatalytic reaction device of the tenth embodiment, described above.
  • the series of vanes 5 generates fluid noise
  • noise is attenuated by the arrangement of the photocatalyst carrier 6 at the inner periphery and the ozone decomposition filters 13 within the discharge ports 3, so the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 14A and Figure 14B are views showing the construction of a photocatalytic reaction device according to a thirteenth embodiment of the present invention.
  • the shape of the casing 1 of the photocatalytic reaction device of this thirteenth embodiment is practically rectangular, when seen in projection from a direction perpendicular to the intake port 2, and discharge ports 3 are arranged in the region of the practically rectangular casing extending from the point of intersection with the side face 1b at the short side, of the side face 1b at the short side and the side face 1c at the long side, up to the point where the distance with respect to the series of vanes 5 of the centrifugal type blower 4 on the downstream side of the fluid is shortest.
  • Figure 15A and Figure 15B are views showing the construction of a photocatalytic reaction device according to a fourteenth embodiment of the present invention.
  • high-voltage terminals 11a, 11b connected with a high-voltage power source are arranged at the inner periphery and outer periphery of the photocatalyst carrier 6.
  • Figure 16A and Figure 16B are views showing the construction of a photocatalytic reaction device according to a fifteenth embodiment of the present invention.
  • deodorizing filters 15 are arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4.
  • deodorizing filters 15 By thus arranging deodorizing filters 15 at the outer periphery of the series of vanes 5 of the centrifugal type blower 4, malodorous constituents in the air such as ammonia or hydrogen sulfide can be absorbed and a decomposition treatment capability displayed that is higher than that of the thirteenth embodiment.
  • ozone decomposition filters could also be employed as these deodorizing filters 15. More specifically, many ozone decomposition filters usually have a deodorizing effect of absorbing malodorous constituents such as ammonia or hydrogen sulfide.
  • the series of vanes 5 generates fluid noise
  • the photocatalyst carrier 6 is arranged at the inner periphery and the deodorizing filters 15 is arranged at the outer periphery, the noise is attenuated and the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 17A and Figure 17B are views showing the construction of a photocatalytic reaction device according to a sixteenth embodiment of the present invention.
  • ultraviolet lamps 14 are arranged at the outer periphery of the photocatalyst carrier 6.
  • ultraviolet light is directed onto the photocatalyst and, in addition, ultraviolet light reflected by the surface of the series of vanes 5 arranged around the lamps 14 is directed onto the photocatalyst.
  • the photocatalytic reaction is promoted and a higher decomposition treatment capability in respect of impurities in the air is displayed than in the case of the thirteenth embodiment.
  • Figure 18A and Figure 18B are views showing the construction of a photocatalytic reaction device according to a seventeenth embodiment of the present invention.
  • ozone decomposition filters 13 are arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4.
  • any ozone generated by the ultraviolet rays that is not used for decomposition is absorbed by the ozone decomposition filters 13 arranged on the inside of the discharge ports 3. Since there is no outflow of excess ozone from the discharge ports 3, sufficient ozone to decompose impurities in the air can be generated and a high decomposition treatment capability as in the fourteenth embodiment is displayed.
  • the series of vanes 5 generates fluid noise
  • the photocatalyst carrier 6 is arranged at the inner periphery and the ozone decomposition filters 13 are arranged at the outer periphery, the noise is attenuated and the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 19A and Figure 19B are views showing the construction of a photocatalytic reaction device according to an eighteenth embodiment of the present invention.
  • ozone decomposition filters 13 are arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4.
  • any ozone generated by the ultraviolet rays that was not used for decomposition is absorbed by the ozone decomposition filters 13 arranged on the inside of the discharge ports 3. Since there is no outflow of excess ozone from the discharge ports 3, sufficient ozone to decompose impurities in the air can be generated and a high decomposition treatment capability as in the sixteenth embodiment is displayed.
  • the series of vanes 5 generates fluid noise
  • the photocatalyst carrier 6 is arranged at the inner periphery and the ozone decomposition filters 13 are arranged at the outer periphery, the noise is attenuated and the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 20A and Figure 20B are views showing the construction of a photocatalytic reaction device according to a nineteenth embodiment of the present invention.
  • the projection of the casing from a direction perpendicular with respect to the intake port 2 formed in the casing 1 is made practically rectangular
  • discharge ports 3 are provided at a plurality of locations on a side face of the casing different from that of the intake port 2 (for example, prescribed locations on the short side face 1b and the long side face 1c)
  • the series of vanes 5 of the centrifugal type blower 4 is arranged around the intake port 2 within the casing
  • a photocatalyst carrier 6 that carries a visible light reaction type photocatalyst is arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4
  • deodorizing filters 15 are arranged on the discharge port 3 side of the photocatalyst carrier 6,
  • the discharge ports 3 are arranged facing the outlet site of the deodorizing filters 15, and portions 1e of the upper face and lower face of the casing 1 facing the photocatalyst carrier 6 are made transparent.
  • the discharge ports 3 are provided in a plurality of locations, the area of the flow paths to the discharge ports 3 is increased in comparison with the prior art case, where a discharge port 3 was provided at a single location only, and higher decomposition treatment capability in respect of impurities in the air is displayed compared with conventionally.
  • Figure 21A and Figure 21B are views showing the construction of a photocatalytic reaction device according to a twentieth embodiment of the present invention.
  • the projection of the casing from a direction perpendicular with respect to the intake port 2 formed in the casing 1 is made practically rectangular
  • discharge ports 3 are provided at a plurality of locations on a side face of the casing different from that of the intake port 2, for example, prescribed locations on the short side face 1b and the long side face 1c
  • the series of vanes 5 of the centrifugal type blower 4 is arranged around the intake port 2 within the casing
  • a photocatalyst carrier 6 that carries a photocatalyst is arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4
  • ozone decomposition filters 13 are arranged on the discharge port side of the photocatalyst carrier
  • the discharge ports 3 are arranged facing the outlet site of the ozone decomposition filters 13, and high-voltage terminals 11a, 11b connected with a high-voltage power source are arranged on the intake port side and the discharge port side of the
  • the photocatalyst carried by the photocatalyst carrier 6 a visible light reaction type photocatalyst, and making at least part of the portions of the casing 1 facing the photocatalyst carrier 6 transparent, a considerable amount of visible light strikes the photocatalyst carrier 6, promoting the photocatalytic reaction and a high decomposition treatment capability in respect of impurities in the air is displayed.
  • the discharge ports 3 are provided in a plurality of locations, the area of the flow paths to the discharge ports 3 is increased in comparison with the prior art case, where a discharge port 3 was provided at a single location only, and higher decomposition treatment capability in respect of impurities in the air is displayed compared with conventionally.
  • Figure 22A and Figure 22B are views showing the construction of a photocatalytic reaction device according to a twenty-first embodiment of the present invention.
  • the projection of the casing from a direction perpendicular with respect to the intake port 2 formed in the casing 1 is made practically rectangular
  • discharge ports 3 are provided at a plurality of locations on a side face of the casing different from that of the intake port 2, for example, prescribed locations on the short side face 1b and the long side face 1c
  • the series of vanes 5 of the centrifugal type blower 4 is arranged around the intake port 2 within the casing
  • a photocatalyst carrier 6 that carries a photocatalyst is arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4
  • ozone decomposition filters 13 are arranged on the discharge port side of the photocatalyst carrier
  • the discharge ports 3 are arranged facing the outlet site of the ozone decomposition filters 13, and ultraviolet lamps 14 are arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4.
  • ultraviolet light is directed onto the photocatalyst carried by the photocatalyst carrier 6 and, in addition, ultraviolet light reflected at the surface of the series of vanes 5 arranged around the lamps 14 is directed onto the photocatalyst carrier by the photocatalyst carrier 6.
  • the photocatalytic reaction is promoted and a higher decomposition treatment capability in respect of impurities in the air is displayed.
  • the photocatalyst carried by the photocatalyst carrier 6 a visible light reaction type photocatalyst, and making at least part of the portions of the casing 1 facing the photocatalyst carrier 6 transparent, a considerable amount of visible light strikes the photocatalyst carrier 6, promoting the photocatalytic reaction and a high decomposition treatment capability in respect of impurities in the air is displayed.
  • the discharge ports 3 are provided in a plurality of locations, the area of the flow paths to the discharge ports 3 is increased in comparison with the prior art case, where a discharge port 3 was provided at a single location only, and higher decomposition treatment capability in respect of impurities in the air is displayed compared with conventionally.
  • Figure 23A and Figure 23B are views showing the construction of a photocatalytic reaction device according to a twenty-second embodiment of the present invention.
  • the photocatalyst carrier 6 provided between the intake port 2 and discharge ports 3 was provided at the inner periphery or outer periphery of the series of vanes 5 of the centrifugal type blower 4 around the intake port 2, but, in this twenty-second embodiment, the photocatalyst carrier 6 is provided facing the intake port 2.
  • an intake port 2 is formed having apertures in the form of a mesh, in the middle of the upper face of a cylindrical casing 1. Also, a plurality of discharge ports 3 having apertures formed in the form of a mesh are formed in a side face of the casing 1 different from that of this intake port 2.
  • the series of vanes 5 of the centrifugal type blower 4 for feeding air flowing in from the intake port 2 to the discharge ports 3 are arranged around the intake port 2 within the casing 1 and a photocatalyst carrier 6 that carries the photocatalyst and is made of a porous body and is for example shaped as a circular plate is arranged on the side of the series of vanes 5 of this centrifugal type blower 4 facing the intake port 2. That is, the photocatalyst carrier 6 is arranged facing the intake port 2 and the series of vanes 5 of the centrifugal type blower 4 is arranged facing the opposite side of this photocatalyst carrier 6 to that of the intake port.
  • high-voltage terminals 11a, 11b that are connected with a high-voltage power source 12 are arranged on both sides of the photocatalyst carrier 6 i.e. at the photocatalyst carrier 6 on the upstream side and downstream side of the inflowing air.
  • a construction is adopted in which discharge ports 3 are arranged on a side face of the casing 1 of the photocatalytic reaction device 9, at least two discharge ports being arranged in directions differing by practically 180° in the radial direction of the series of vanes 5 of the centrifugal type blower 4, or a plurality of discharge ports being arranged around the centrifugal type blower 4, or the discharge ports being arranged in continuous fashion along the entire circumferential surface of the side face of the casing 1.
  • the partition 20 that was conventionally present in the vicinity of the series of vanes 5 is absent, so the fan characteristic is shifted from C0 to C1 i.e. towards larger flow rate and larger static pressure.
  • the airflow resistance is reduced by the increase of area of the flow paths to the discharge ports 3, being reduced from R0 to R1.
  • the operating flow rate is increased from the conventional value of Q0 to Q1 and a higher decomposition treatment capability in respect of impurities in the air than conventionally is displayed.
  • ultraviolet light is generated by discharge between the high-voltage terminals 11a and 11b, promoting the decomposition action of the photocatalyst. The ozone that is then generated by the ultraviolet light performs oxidative decomposition of impurities in the air.
  • Figure 24A and Figure 24B are views showing the construction of a photocatalytic reaction device according to a twenty-third embodiment of the present invention.
  • a photocatalytic reaction device has a construction in which ozone decomposition filters 13 are arranged on the inside of these discharge ports 3 in the twenty-second embodiment described above.
  • the decomposition action of the photocatalyst is promoted by generation of ultraviolet light by discharge between the high-voltage terminals 11a and 11b.
  • the ozone that is then generated by the ultraviolet light performs oxidative decomposition of impurities in the air.
  • Ozone that was not used in the decomposition is absorbed by the ozone decomposition filters 13.
  • sufficient ozone to decompose the impurities in the air can be generated, so that a decomposition treatment capability higher than that of the photocatalytic reaction device of the twenty-second embodiment, described above is displayed.
  • the series of vanes 5 generates fluid noise
  • noise is attenuated by the arrangement of the photocatalyst carrier 6 and the side of the intake port 2 and the ozone decomposition filters 13 at the side of the discharge ports 3, so the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 25A and Figure 25B are views showing the construction of a photocatalytic reaction device according to a twenty-fourth embodiment of the present invention.
  • the lower Figure is a view showing a cross-section viewed in the direction of the arrows at the position of a diagonal of a practically square casing 1 in the upper Figure.
  • the shape of the casing in a projection of the shape of the casing from a direction perpendicular to the intake port, is practically square instead of being circular as in the case of the twenty-second embodiment described above, and the discharge ports 3 are arranged at the corners of this practically square casing.
  • the casing 1 By making the casing 1 practically square in projection from the direction perpendicular to the intake port 2 and arranging the discharge ports 3 at the corners of this practically square casing 1, the air pressure at the corners is increased by the air flowing out from the series of vanes 5, so that the air flows out smoothly from the discharge ports 3.
  • the flow rate is practically unchanged and the device therefore shows a decomposition treatment capability in respect of impurities in the air that is on the same level with that of the twenty-second embodiment.
  • Figure 26A and Figure 26B are views showing the construction of a photocatalytic reaction device according to a twenty-fifth embodiment of the present invention.
  • the power source 8 for the motor of the centrifugal type blower 4 is arranged at a corner of the practically square casing 1.
  • the power source 8 for the motor of the centrifugal type blower 4 By arranging the power source 8 for the motor of the centrifugal type blower 4 at a corner of the practically square casing 1, the air flowing out from the discharge ports 3 after flowing out from the series of vanes 5 flows through the vicinity of the power source 8 for the motor. As a result, cooling of the electronic components that generate heat that are provided in the power source is promoted, increasing reliability.
  • Figure 27A and Figure 27B are views showing the construction of a photocatalytic reaction device according to a twenty-sixth embodiment of the present invention.
  • ozone decomposition filters 13 are arranged at the corners of the practically square casing 1.
  • any ozone generated by the ultraviolet rays that is not used in decomposition is absorbed by the ozone decomposition filters 13 arranged on the inside of the discharge ports 3. Since no excess ozone flows out from the ozone discharge ports 3, sufficient ozone can be generated to decompose the impurities in the air and a higher decomposition treatment capability is displayed than that of the twenty-fifth embodiment.
  • Figure 28A and Figure 28B are views showing the construction of a photocatalytic reaction device according to a twenty-seventh embodiment of the present invention.
  • the shape of the casing 1 of the photocatalytic reaction device of this twenty-seventh embodiment is practically rectangular, when seen in projection from a direction perpendicular to the intake port 2, and the discharge ports 3 are arranged in the region of the practically rectangular casing extending from the point of intersection with the side face 1b at the short side, of the side face 1b at the short side and the side face 1c at the long side, up to the point where the distance with respect to the series of vanes 5 of the centrifugal type blower 4 on the downstream side of the fluid is shortest.
  • the casing 1 of the photocatalytic reaction device practically rectangular in this way, when seen in projection from a direction perpendicular to the intake port 2, and arranging the discharge ports 3 in the region 1d of the practically rectangular casing 1 extending from the point of intersection with the side face 1b at the short side, of the side face 1b at the short side and the side face 1c at the long side, up to the point where the distance with respect to the series of vanes 5 of the centrifugal type blower 4 on the downstream side of the fluid is shortest, the air pressure between the series of vanes 5 and the discharge ports 3 is raised by the air flowing out from the series of vanes 5 but the flow speed becomes smaller due to the wider space than in the case of the twenty-fourth embodiment: as a result, the air flows out smoothly from the discharge ports 3. As a result, the flow rate is increased due to the small airflow resistance and a higher decomposition treatment capability in respect of impurities in the air is displayed than in the case of the twenty-fourth embodiment.
  • Figure 29A and Figure 29B are views showing the construction of a photocatalytic reaction device according to a twenty-eighth embodiment of the present invention.
  • deodorizing filters 15 are arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4.
  • deodorizing filters 15 By thus arranging deodorizing filters 15 for example in the vicinity of a discharge ports 3 at the outer periphery of the series of vanes 5 of the centrifugal type blower 4, malodorous constituents such as ammonia or hydrogen sulfide in the air can be absorbed and a higher decomposition treatment capability than in the case of the twenty-seventh embodiment is displayed.
  • ozone decomposition filters could be employed as these deodorizing filters 15. More specifically, many ozone decomposition filters usually have a deodorizing effect of absorbing malodorous constituents such as ammonia or hydrogen sulfide.
  • the series of vanes 5 generates fluid noise
  • noise is attenuated by the arrangement of the photocatalyst carrier 6 at the side of the intake port 2 and the deodorizing filters 15 at the outer periphery thereof, so the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 30A and Figure 30B are views showing the construction of a photocatalytic reaction device according to a twenty-ninth embodiment of the present invention.
  • ozone decomposition filters 13 are arranged at the outer periphery of the series of vanes 5 of the centrifugal type blower 4.
  • any ozone generated by the ultraviolet rays that is not employed in decomposition is absorbed by the ozone decomposition filters 13 arranged within the discharge ports 3.
  • the device according to this embodiment shows a decomposition treatment capability higher than that of the photocatalytic reaction device of the twenty-seventh embodiment.
  • the series of vanes 5 generates fluid noise
  • noise is attenuated by the arrangement of the photocatalyst carrier 6 on the side of the intake port 2 and the ozone decomposition filters 13 at the outer periphery, so the noise that is propagated to outside the casing 1 can be reduced.
  • Figure 31A and Figure 31B are views showing the construction of a photocatalytic reaction device according to a thirtieth embodiment of the present invention.
  • the projection of the casing from a direction perpendicular with respect to the intake port 2 formed in the casing 1 is practically rectangular and the series of vanes 5 of the centrifugal type blower 4 are arranged around the intake port 2 on the inside of the casing, discharge ports 3 being provided at a plurality of locations, for example prescribed locations of the short side face 1b and the long side face 1c, on a side of the casing different from that of the intake port 2; a photocatalyst carrier 6 that carries a visible light reaction type photocatalyst is arranged on the side of the intake port 2 of the series of vanes 5 of the centrifugal type blower 4; deodorizing filters 15 are arranged on the side of the discharge ports 3 of the photocatalyst carrier 6; and the portion (including a mesh-shaped portion of the intake port 2) of the upper surface at the surface of the casing 1 facing the discharge ports 3 on the outlet side of the deodorizing filters 15 and
  • the photocatalytic reaction is promoted by visible light striking the photocatalyst carrier 6 and high decomposition treatment capability is displayed in respect of impurities in the air.
  • the area of the flow path to the discharge ports 3 is increased compared with conventionally, where the discharge port 3 was provided in only a single location and a higher decomposition treatment capability is displayed than conventionally in respect of impurities in the air.

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  • Engineering & Computer Science (AREA)
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EP04025764A 2003-10-31 2004-10-29 Dispositif pour la purification photocatalytique de l'air Expired - Fee Related EP1527809B1 (fr)

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JP2003371609 2003-10-31
JP2003371609 2003-10-31
JP2004099611A JP2005152584A (ja) 2003-10-31 2004-03-30 光触媒反応装置。
JP2004099611 2004-03-30

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2892951A1 (fr) * 2005-11-10 2007-05-11 Alcion Environnement Sarl Dispositif de traitement d'un gaz par photocatalyse
WO2007131614A1 (fr) * 2006-05-11 2007-11-22 Fraunhofer-Gesellschaft Zur Förderung Der Angewandten Forschung Composant pour l'absorption de bruit et le traitement de l'air
EP2529759A1 (fr) * 2011-06-03 2012-12-05 Virobuster GmbH Appareil et procédé d'inactivation d'allergènes protéinogènes
ITUB20153685A1 (it) * 2015-09-17 2017-03-17 Univ Politecnica Delle Marche Dispositivo e processo per la purificazione dell?aria

Families Citing this family (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2005152584A (ja) 2003-10-31 2005-06-16 Toshiba Corp 光触媒反応装置。
US8585980B2 (en) * 2010-09-07 2013-11-19 Puradigm, Llc Enhanced photo-catalytic cells
CN105642037B (zh) * 2016-03-03 2017-12-19 广东美的制冷设备有限公司 过滤器及具有其的净化器
CN109312940A (zh) * 2016-06-08 2019-02-05 卓胜镐 空气净化器
JP7228352B2 (ja) * 2018-09-04 2023-02-24 株式会社日立製作所 移動型空気清浄機
WO2021145483A1 (fr) * 2020-01-16 2021-07-22 콤마 주식회사 Purificateur d'air
US11724001B2 (en) * 2020-01-23 2023-08-15 Aerus Medical, Llc Air purification and sterilization unit
DE102020130827B4 (de) 2020-11-21 2023-08-17 Malte Zeitnitz Fluidreinigungsmodul und Fluidreinigungssystem

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000097452A (ja) * 1998-09-24 2000-04-04 Topre Corp セントラル換気ユニット
JP2000315420A (ja) * 1999-04-30 2000-11-14 Shimadzu Corp 空気清浄機能付照明装置
JP2000325446A (ja) * 1999-05-19 2000-11-28 Tiger Vacuum Bottle Co Ltd 空気清浄機
JP2002253662A (ja) * 2001-03-05 2002-09-10 Koji Tanaka 車両用空気清浄器
EP1258281A2 (fr) * 2001-05-17 2002-11-20 Kabushiki Kaisha Toshiba Electrode de décharge et appareil photocatalytique
EP1262100A1 (fr) * 2000-03-06 2002-12-04 Fumakilla Limited Dispositif diffuseur de produits chimiques de type ventilateur
JP2003240285A (ja) * 2002-02-19 2003-08-27 Denso Corp 空気清浄器
EP1348448A1 (fr) * 2000-08-28 2003-10-01 Sharp Kabushiki Kaisha Dispositif de purification de l'air et generateur d'ions utilise pour ce dispositif
JP2004100585A (ja) * 2002-09-10 2004-04-02 Denso Corp 遠心式送風機
JP2004181301A (ja) * 2002-11-29 2004-07-02 Shimadzu Corp 触媒ハニカムおよび空気清浄機

Family Cites Families (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4892712A (en) * 1987-09-04 1990-01-09 Nutech Energy Systems Inc. Fluid purification
JPH11335187A (ja) 1998-05-25 1999-12-07 Toshiba Corp 光触媒モジュール及び光触媒装置
JP3754601B2 (ja) * 2000-06-16 2006-03-15 株式会社東芝 冷蔵庫
US7056476B2 (en) * 2000-06-15 2006-06-06 Kabushiki Kaisha Toshiba Refrigerator and deodorizer producing ozone by high-voltage discharge
KR200244008Y1 (ko) * 2001-05-14 2001-10-15 주식회사 엔비오 공기청정기
KR20020095846A (ko) * 2001-06-16 2002-12-28 (주)펩콘 공기 정화용 조명 장치
JP2003070888A (ja) * 2001-09-06 2003-03-11 Denso Corp 空気清浄装置
JP2003106581A (ja) * 2001-09-28 2003-04-09 Fujitsu General Ltd 空気清浄機
JP2003185180A (ja) * 2001-12-12 2003-07-03 Sanyo Electric Co Ltd 空気調和機
CN2682321Y (zh) * 2003-08-29 2005-03-02 李鹏 空气净化除菌装置
JP2005152584A (ja) 2003-10-31 2005-06-16 Toshiba Corp 光触媒反応装置。

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2000097452A (ja) * 1998-09-24 2000-04-04 Topre Corp セントラル換気ユニット
JP2000315420A (ja) * 1999-04-30 2000-11-14 Shimadzu Corp 空気清浄機能付照明装置
JP2000325446A (ja) * 1999-05-19 2000-11-28 Tiger Vacuum Bottle Co Ltd 空気清浄機
EP1262100A1 (fr) * 2000-03-06 2002-12-04 Fumakilla Limited Dispositif diffuseur de produits chimiques de type ventilateur
EP1348448A1 (fr) * 2000-08-28 2003-10-01 Sharp Kabushiki Kaisha Dispositif de purification de l'air et generateur d'ions utilise pour ce dispositif
JP2002253662A (ja) * 2001-03-05 2002-09-10 Koji Tanaka 車両用空気清浄器
EP1258281A2 (fr) * 2001-05-17 2002-11-20 Kabushiki Kaisha Toshiba Electrode de décharge et appareil photocatalytique
JP2003240285A (ja) * 2002-02-19 2003-08-27 Denso Corp 空気清浄器
JP2004100585A (ja) * 2002-09-10 2004-04-02 Denso Corp 遠心式送風機
JP2004181301A (ja) * 2002-11-29 2004-07-02 Shimadzu Corp 触媒ハニカムおよび空気清浄機

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
PATENT ABSTRACTS OF JAPAN vol. 2000, no. 07 29 September 2000 (2000-09-29) *
PATENT ABSTRACTS OF JAPAN vol. 2000, no. 14 5 March 2001 (2001-03-05) *
PATENT ABSTRACTS OF JAPAN vol. 2003, no. 01 14 January 2003 (2003-01-14) *
PATENT ABSTRACTS OF JAPAN vol. 2003, no. 12 5 December 2003 (2003-12-05) *

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR2892951A1 (fr) * 2005-11-10 2007-05-11 Alcion Environnement Sarl Dispositif de traitement d'un gaz par photocatalyse
WO2007131614A1 (fr) * 2006-05-11 2007-11-22 Fraunhofer-Gesellschaft Zur Förderung Der Angewandten Forschung Composant pour l'absorption de bruit et le traitement de l'air
EP2529759A1 (fr) * 2011-06-03 2012-12-05 Virobuster GmbH Appareil et procédé d'inactivation d'allergènes protéinogènes
ITUB20153685A1 (it) * 2015-09-17 2017-03-17 Univ Politecnica Delle Marche Dispositivo e processo per la purificazione dell?aria
WO2017046825A1 (fr) * 2015-09-17 2017-03-23 Universita' Politecnica Delle Marche Dispositif et procédé de purification d'air
RU2717798C2 (ru) * 2015-09-17 2020-03-25 Университа Политекника Делле Марке Устройство и способ очистки воздуха

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EP1527809B1 (fr) 2007-03-14
JP2005152584A (ja) 2005-06-16
US7507383B2 (en) 2009-03-24
CN100574815C (zh) 2009-12-30
US20050152812A1 (en) 2005-07-14
KR20050041957A (ko) 2005-05-04
CN1611269A (zh) 2005-05-04
KR100620882B1 (ko) 2006-09-19
DE602004005286D1 (de) 2007-04-26
DE602004005286T2 (de) 2007-12-20

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